A Rapid imethod Test for Screening Pesticides V.2.0 for Cliquid Software

Similar documents
Pesticides in Cannabis

Multiresidue Analysis of 100 Pesticides in Food Samples by LC/Triple Quadrupole Mass Spectrometry Application

dynamic MRM for pesticide analysis

Higher Confidence in Identification with QTRAP LC/MS/MS Systems when Screening and Quantifying Pesticides in Fruit and Vegetable Samples

Pure Chromatography. Food Safety Applications. Abstract. Introduction

Multi-residue Method for Agricultural Chemicals by GC-MS (Animal and Fishery Products)

Screening Validation Report 1

Safeguarding Food from Pesticides by UHPLC After Extraction with the QuEChERS Method

Screening for 250 Pesticides in Orange Oil and Ginseng Extract by LC-MS/MS Using TraceFinder Software

Batch 1. Batch 2. Batch 3. Batch 4. Batch 5

Analysis of Pesticides in Citrus Oil Using a Shimadzu GCMS-TQ8030. No. GCMS No. SSI-GCMS-1404

Determination of pesticides in baby food by UHPLC/MS/MS using the Agilent 1290 Infinity LC system and the Agilent 6460 triple quadrupole LC/MS

Determination of Pesticide Multiresidues in Apple, Pear and Grape using modified QuEChERS and analysis by LC-QTOF MS

DETERMINATION OF PESTICIDES IN FOOD USING UPLC WITH POLARITY SWITCHING TANDEM QUADRUPOLE LC/MS/MS

Application Note. Abstract. Authors. Food Safety and Environmental

Overview. Introduction

Analytical considerations on the use of a fruit-specific and representative matrix in pesticide residue analysis by LC-ESI-MS/MS

Liquid Chromatography Mass Spectrometry. Expanding Capabilities in Multi-Residue Pesticide Analysis Using The LCMS-8060

Advanced Data Acquisition and Data Processing Workflows to Identify, Quantify and Confirm Pesticide Residues

Overview. Introduction. Method Details. André Schreiber and Yun Yun Zou AB SCIEX, Concord, Ontario, Canada

Using the MRM Catalogue of Cliquid Software to Quickly Build LC-MS/MS Methods for Pesticide Analysis Matching the Japanese Positive List

Food & Environmental. Overview. Introduction. Method Details. André Schreiber and Yun Yun Zou SCIEX, Concord, Ontario, Canada

LC-MS/MS multiresidue method used for pesticides analysis in fruits and vegetables

Application of a Triggered MRM Database and Library for the Quantitation and Identification of Pesticides in Food Extracts

Analysis of Pesticides in Baby Foods Using a Triple-Quadrupole GC/MS/MS

We are IntechOpen, the first native scientific publisher of Open Access books. International authors and editors. Our authors are among the TOP 1%

Triumphs and Challenges of High-Resolution Mass Spectrometry in Comprehensive Residue Screens

Determination of Pesticide Residues in Oats by Automated. QuEChERS and LC/QQQ. Application Note. Abstract. Introduction

High Throughput Multi-Residue Screening of Drinking Water using the SPE-DEX~ and Pegasus GC-TOF-MS

Analyst Software. Automatic Optimization Tutorial

Utility of H-SRM to Reduce Matrix Interference in Food Residue Analysis of Pesticides by LC-MS/MS Using the TSQ Quantum Discovery

EPA Method 535: Detection of Degradates of Chloroacetanilides and other Acetamide Herbicides in Water by LC/MS/MS

Simplified Workflow and Improved Confidence in Screening Methods on Time of Flight Mass Spectrometry

Application Note. Author. Abstract. Food Testing & Agriculture. Edgar Naegele Agilent Technologies, Inc. Waldbronn, Germany

Schedule of Accreditation issued by United Kingdom Accreditation Service 2 Pine Trees, Chertsey Lane, Staines-upon-Thames, TW18 3HR, UK

Ultra-fast screening of pesticides in foods and agricultural products with desorption corona beam ionization (DCBI) tandem mass spectrometry

Fast GC-MS/MS for High Throughput Pesticides Analysis

Application Note. Abstract. Authors. Environmental

Summary of results, after removal of outliers

Official Journal of the European Union L 328/9

Dairy National Chemical Contaminants Programme Raw Milk Result Summary July 2014 to June 2015

László Tölgyesi LC/MS scientist EFSC Demo Group. International Symposium on Food Safety and Quality: Applications of Nuclear and Related Techniques

Analytical Test Report 10

COMMISSION REGULATION (EU)

Rapid Screening and Confirmation of Melamine Residues in Milk and Its Products by Liquid Chromatography Tandem Mass Spectrometry

Routine Multiresidue Pesticide Analysis using the Agilent 6470 Triple Quadrupole Mass Spectrometer

Available online at Journal of Chromatography A, 1175 (2007) 24 37

Automated Screening of 600 Pesticides in Food by LC/TOF MS Using a Molecular-Feature Database Search Application

Multiclass Determination of Organic Contaminants in Red Chili and Turmeric Powders

Pesticides Analysis Using the Agilent 5977A Series GC/MSD

Validation of a Simple and Rapid Multiresidue Method (QuEChERS) and its Implementation in Routine Pesticide Analysis

Multi pesticide residue analysis in tobacco by GCMS/MS using QuEChERS as an extraction method

EPA Method 535: Detection of Degradates of Chloroacetanilides and other Acetamide Herbicides in Water by LC/MS/MS

Quantitative Analysis and Identification of Migrants in Food Packaging Using LC-MS/MS

Improved GC/MS Analysis of Tomato Pesticides with Agilent Deactivated Silica Tubing

Qualitative and Quantitative Analysis of Pesticides in Horse Feed Matrix Using Orbitrap MS

Charles Yang, Dipankar Ghosh, Jonathan Beck Thermo Fisher Scientific, San Jose, CA, USA

Non-targeted Screening and Accurate Mass Confirmation of 510 Pesticides on the High Resolution Exactive Benchtop LC/MS Orbitrap Mass Spectrometer

Sensitive and Repeatable Analysis of Pesticides in QuEChERS Extracts with APGC-MS/MS

Almería 23 rd -25 th October th Joint Workshop of the European Union Reference Laboratories for Residues of Pesticides

Screening Method for 30 Pesticides in Green Tea Extract Using Automated Online Sample Preparation with LC-MS/MS

Evaluation of interferences between matrix-analyte for the correct identification of the pesticides by GC-QqQ-MS/MS and LC-QqQ-MS/MS

GC/Q-TOF MS Surveillance of Pesticides in Food

Quantitative and Qualitative Confirmation of Pesticides in Beet Extract Using a Hybrid Quadrupole-Orbitrap Mass Spectrometer

CHROMABOND HLB. Introduction. Advantages of CHROMABOND HLB. Technical data

LC-MS/MS and GC-MS/MS Multi Residue Pesticide Analysis in Fruit and Vegetable Extracts on a Single Tandem Quadrupole Mass Spectrometer

Multi-residue analysis of pesticides in crude food extracts using a simple extraction technique and LC/MS/MS

LC/MS/MS Analysis of Pesticide Residues in Apples Using Agilent Chem Elut Cartridges

2016 iquan Series: Pesticide Quantitation on the Thermo Scientific TSQ Quantiva

Waters Application Notes. Food Testing

Characterization of Carbon SPE for the Extraction of Polar Analytes

[ APPLICATION NOTE ] UPLC and APGC Multi Residue Pesticide Analysis on a Single Tandem Quadrupole Mass Spectrometer Platform APPLICATION BENEFITS AIM

Three-Fold Increase in Productivity for Pesticide Residue Analysis in Baby Food Using Fast Triple Quadrupole GC-MS/MS

Validation Report 8 Determination of pesticide residues in rice and wheat by GC-MS/MS and LC-MS/MS (QuEChERS method) Appendix 2

Drinking-Water Systems Regulation O. Reg. 170/03

For the detection and quantitation of glyphosate in water (groundwater, surface water, well water).

Quick, Easy, Cheap, Effective, Rugged and Safe (QuEChERS) Approach for Determining Pesticide Residues

The Analysis of Organophosphate Pesticides by LC/MS Application

Thermo Scientific Accucore XL HPLC Columns. Technical Manual

Introducing the Agilent G6410A Triple Quadrupole Mass Spectrometer

Almería 23 rd -25 th October th Joint Workshop of the European Union Reference Laboratories for Residues of Pesticides

Pesticide LC/MS/MS Library Version 1.0 for Cliquid Software

QuEChERS Pesticide Analysis for Fresh Produce*

Rapid Pesticide Screening and Identification Using the High Resolution All Ions MS/MS Technique

Tyler Trent, Applications Sales Specialist, Teledyne Tekmar P a g e 1

Application Note. Abstract. Authors. Food Testing and Agriculture

The Quantitation and Identification of Coccidiostats in Food by LC-MS/MS using the AB SCIEX 4000 Q TRAP System

Anaylsis of Pesticide Residues in Rice Using Agilent Bond Elut QuEChERS AOAC Kit by LC-MS/MS Detection

The development and inter-laboratory verification of LC MS libraries for organic chemicals of environmental concern

Index 1 Residual Pesticides 3 Food Additives 4 Others 2 Veterinary Drugs (Antibiotics and Synthetic Antibacterials) 5 Reference Materials

Analyst Software. Peptide and Protein Quantitation Tutorial

Overview. Introduction. André Schreiber 1 and Yun Yun Zou 1 1 AB SCIEX, Concord, Ontario, Canada

Analysis of Pesticides and Contaminants using HS-SPME-GC/MS and DRS Detection. Blair Surridge, Tyler Dyer, Rene Bilideau, Paloma Bertolin Presoti

The Pulsed Flame Photometric Detector for analysis of phosphorus pesticides in wastewater and food commodities

Screening of pesticides in water using SPE on line

Application Note LCMS-110 Development of a Targeted Quantitative LC-MS/MS Method for 431 Positive and Negative Ion Pesticides in a Single Analysis

(12) Patent Application Publication (10) Pub. No.: US 2003/ A1

Advantages of Reversed Sandwich Injection for Pesticide Residue Analysis

Comprehensive Pesticide Analysis in Juice Using a Combination of GC/MS and LC/MS Methods

European Reference Laboratory - FV

Transcription:

A Rapid imethod Test for Screening Pesticides V.2.0 for Cliquid Software imethods Test Pesticides Screening Version 2.0 for Cliquid Software With more than 800 pesticides currently in use there is growing concern by government agencies about the effect of pesticide exposure on human health. As a result, the residue level of pesticides in food, water and other consumer products are highly regulated. While analytical techniques like GC or GC/MS have traditionally been used for pesticide analysis, LC/MS/MS has quickly become the technique of choice due to the ability to analyze a more diverse set of pesticides, faster with better sensitivity and less sample preparation. The following description outlines the instrument requirements and expected results obtainable from the AB SCIEX imethod Test for Pesticide Screening and Quantitation using an AB SCIEX 3200 QTRAP system or API 3200 system. This imethod test consists of a pre-configured method to screen for 494 pesticides and individual quantitation methods for carbamate, phenyl urea, triazine, organophosphorus, and acidic pesticides. All methods have also been verified for use on AB SCIEX 4000 QTRAP, API 4000, QTRAP 5500 and AB SCIEX TripleQuad 5500 systems. More in-depth sample preparation, and instrument parameter information is included as part of the standard operating procedure provided with the method, as are the required analytical columns. Solvents, standards and any supplies required for sample preparation are not included. Please note that the use of QTRAP system technology is recommended for use with the screening method provided and that the associated library is not included and must be purchased separately. XIC of +MRM (517 pairs): 207.0/161.0 amu Expected RT: 0.8 I... Max. 75.8 cps. 1.20e5 1.00e5 Intensity, cps 8.00e4 6.00e4 4.00e4 2.00e4 0.00 0.55 0.82 11.03 11.20 11.49 12.12 2 4 6 8 10 12 Time, min Figure 1: Chromatogram of a 303 pesticides mix on an API 3200 LC/MS/MS system (10 ng/ml) p 1

The pesticide screening method included in this imethod test is for the routine screening of 494 pesticides from food samples using the QuEChERS extraction and cleanup technique. The method uses external calibration standards and matrix spike recoveries to correct for sample and instrument variability and is based upon the use of a 3200 QTRAP LC/MS/MS system. A suggested method for the extraction of pesticides from vegetable, nut and citrus plant materials is also provided and is based upon the use of Restek QuEChERS tubes. Separation is achieved using a simple methanol / water gradient with ammonium formate with a Phenomenex Synergi 2.5 µm Fusion 100 Å, 50 x 2 mm HPLC column that is included with this imethod test. Table 1 provides representative recoveries, signal-to-noise ratios and estimated detection limits for 130 selected pesticides spiked at 25 ng/ml in a cucumber matrix using QuEChERS sample processing technique. Table 1. Representative recoveries, signal-to-noise ratios and estimated detection limits for 130 selected pesticides spiked at 25 ng/ml in a cucumber matrix using QuEChERS sample processing, as run on the 3200 QTRAP LC/MS/MS system Analyte % Recovery S/N * % CV Estimated detection limit (ng/ml) Aldicarb-sulfoxide 97.0% 26 4.2% 9.6 Aldoxycarb 96.4% 33.2 10.0% 7.5 Alloxydim 60.8% 32.2 7.5% 7.8 Aminocarb 84.2% 84 2.6% 3.0 Atrazine 65.1% 34 2.4% 7.4 Atrazine-2-hydroxy 79.9% 77.8 2.9% 3.2 Atrazine-desethyl-2-hydroxy 104.1% 38.8 1.9% 6.4 Benalaxyl 94.9% 39.5 18.1% 6.3 Bendiocarb 120.2% 33.1 16.2% 7.6 Benzoximate 119.9% 29.3 10.0% 8.5 Boscalid 15.3% 14.3 18.7% 17.5 Bromacil 99.0% 15.9 8.4% 15.7 Bupirimate 106.2% 43.8 9.0% 5.7 Butocarboxim-sulfoxid 102.2% 37.7 2.3% 6.6 Buturon 98.6% 20.4 4.1% 12.3 Carbaryl 98.4% 44.7 1.5% 5.6 Carbetamide 94.3% 58.8 4.9% 4.3 Chloridazon 111.1% 35.5 1.7% 7.0 Chlorotoluron 149.2% 38.1 2.4% 6.6 Chloroxuron 69.5% 24.7 11.0% 10.1 Cinosulfuron 88.6% 28.8 18.9% 8.7 Clomazone 107.2% 42.3 1.8% 5.9 Cloquintocet-mexyl 140.8% 95.8 10.1% 2.6 Coumaphos 120.8% 24.4 3.6% 10.2 Cyanazine 115.6% 22.1 20.1% 11.3 Cyproconazole 48.6% 24.6 7.1% 10.2 Cyprodinil 120.2% 11.3 7.6% 22.1 Demeton-S-methyl-sulfone 90.0% 32.8 1.9% 7.6 Diazinon 100.5% 81.9 7.2% 3.1 Diclobutrazol 88.3% 26.3 7.6% 9.5 Dicrotophos 112.7% 58.1 19.1% 4.3 Diethofencarb 28.5% 16.2 8.0% 15.4 Difenoxuron 104.0% 51 5.3% 5.0 Dimefuron 92.5% 20 6.6% 12.6 Dimethachlor 88.8% 13 11.8% 19.5 Dimethenamide 100.5% 39 2.7% 6.5 Dimetilan 106.0% 101 2.5% 2.5 Dodemorph 67.0% 107 3.0% 2.3 Ethidimuron 139.0% 28 6.5% 8.9 Ethiofencarb-sulfon 113.0% 59 14.7% 4.3 Ethiofencarb-sulfoxid 99.1% 119 3.6% 2.1 p 2

Analyte % Recovery S/N * % CV Estimated detection limit (ng/ml) Ethion 113.9% 17 7.2% 14.8 Ethirimol 99.6% 42 4.9% 6.0 Ethoprophos 112.9% 16 14.1% 15.2 Etrimfos 93.3% 64 4.6% 3.9 Fenbuconazole 93.0% 21 2.2% 11.9 Fenfuram 98.0% 46 7.7% 5.5 Fenhexamid 47.9% 15 15.1% 17.0 Fenoxaprop-P-ethyl 113.9% 32 7.2% 7.8 Fenpropimorph 130.8% 152 4.2% 1.6 Fenpyroximate 161.6% 15 8.4% 16.8 Fenuron 102.8% 47 5.5% 5.3 Flamprop-M-isopropyl 104.1% 55 4.1% 4.5 Flamprop-M-methyl 90.2% 20 3.7% 12.4 Flazasulfuron 100.8% 74 7.5% 3.4 Fluazifop-butyl 144.5% 50 3.6% 5.0 Flufenacet 89.7% 22 12.8% 11.5 Fluometuron 120.9% 77 2.3% 3.2 Fluridone 68.4% 30 11.8% 8.4 Flurtamone 89.7% 20 5.2% 12.3 Fuberidazole 102.7% 125 6.2% 2.0 Haloxyfop-P-methyl 106.4% 15 3.2% 16.9 Hexaconazole 100.9% 23 2.1% 11.0 Hexazinone 106.3% 202 15.8% 1.2 Imazalil 117.7% 34 18.1% 7.3 Isazofos 74.9% 13 8.0% 19.1 Isoprothiolane 62.1% 77 1.2% 3.2 Lenacil 111.3% 43 6.1% 5.8 Malaoxon 44.7% 50 9.5% 5.0 Malathion 94.7% 30 5.9% 8.3 Mepanipyrim 79.5% 3 7.9% 80.6 Metconazole 118.2% 19 7.3% 13.4 Methamidophos 90.9% 33 6.5% 7.6 Methfuroxam 66.2% 96 1.1% 2.6 Methidathion 47.9% 35 4.2% 7.2 Metobromuron 116.1% 19 4.0% 12.9 Metolachlor 82.7% 22 2.6% 11.4 Metosulam 99.7% 51 2.7% 4.9 Monuron 100.3% 22 2.8% 11.6 Napropamide 103.7% 31 11.5% 8.1 Oxasulfuron 87.8% 78 6.6% 3.2 Oxycarboxin 98.5% 110 5.3% 2.3 Paclobutrazol 105.4% 48 9.2% 5.2 Phosalone 102.9% 13 9.0% 18.9 Phosphamidon 95.2% 104 6.5% 2.4 Picoxystrobin 133.1% 104 3.8% 2.4 Pirimiphos-ethyl 129.7% 57 4.1% 4.4 Pirimiphos-methyl 105.1% 63 3.1% 4.0 Prometon 100.5% 105 6.0% 2.4 Prometryne 49.5% 14 19.5% 18.4 Propamocarb 106.5% 20 1.9% 12.8 Propazin-2-hydroxy 81.5% 19 3.6% 12.9 Propazine 72.8% 11 10.7% 22.5 Prosulfocarb 114.9% 145 6.1% 1.7 Pymetrozine 101.4% 115 2.6% 2.2 p 3

Analyte % Recovery S/N * % CV Estimated detection limit (ng/ml) Pyraclostrobin 141.1% 24 9.6% 10.5 Pyrazophos 108.9% 55 4.8% 4.5 Pyridaben 102.8% 18 4.1% 14.1 Pyridaphenthion 88.6% 10 6.3% 25.3 Pyrimethanil 40.1% 18 5.8% 13.6 Pyriproxyfen 153.8% 51 4.3% 4.9 Quinalphos 124.9% 17 7.3% 14.8 Quinmerac 104.9% 116 1.3% 2.2 Sebuthylazine 56.9% 55 3.6% 4.6 Sebuthylazine-desethyl 88.6% 39 7.1% 6.5 Sethoxydim 82.5% 28 10.1% 8.9 Siduron 59.7% 14 5.3% 17.5 Simazine-2-hydroxy 105.5% 99 10.6% 2.5 Simetryn 95.7% 96 6.6% 2.6 Spiroxamine 97.1% 230 6.0% 1.1 Sulfometuron-methyl 98.2% 103 5.1% 2.4 Tebuconazol 87.3% 45 9.6% 5.5 Tebufenpyrad 125.2% 13 10.6% 18.8 Tebutam 87.2% 22 7.3% 11.4 Tebuthiuron 97.8% 61 14.4% 4.1 Terbufos 44.3% 4 20.3% 65.8 Terbuthylazine 31.7% 18 3.3% 14.1 Terbuthylazine-desethyl 88.7% 39 8.1% 6.5 Terbutryn 31.9% 119 6.0% 2.1 Tetrachlorvinphos 101.3% 20 8.7% 12.5 Tetraconazole 82.1% 32 16.3% 7.8 Thifensulfuron-methyl 100.8% 74 4.2% 3.4 Triasulfuron 80.5% 35 7.5% 7.2 Triazophos 31.9% 19 9.9% 13.2 Tricyclazole 93.8% 72 1.9% 3.5 Trietazine 75.4% 12 13.6% 21.0 Trifloxystrobin 113.9% 83 5.8% 3.0 Triflumizole 122.4% 25 11.9% 10.1 Triticonazole 117.1% 24 5.8% 10.6 Uniconazole 66.5% 24 24.0% 10.6 Vamidothion 113.1% 36 13.9% 7.0 * Signal-to-noise obtained at three standard deviations on a 3200 QTRAP System. Estimated detection limit based on estimated signal at 10 x the Signal-to-noise ratio. Quantitation Methods The following information outlines the list of standard compounds that in each of the quantitation methods for each compound class listed above. The methodology presented below was developed to quantify each pesticide when run by compound class, at < 10 ppb in order to meet regulatory requirements. The 603-compound MRM catalogue provided can also be used to create new customized tests according to any combinations required. Example sample preparation procedures are provided for fruits and vegetables, based upon a simple sample homogenization, centrifugation, extraction and dilution. These procedures may require additional optimization based upon the actual composition and consistency of the fruit or vegetable under investigation. Deuterated and/or C13-labeled internal standards of known concentrations are added during sample preparation to monitor sample recovery. p 4

Figure 2: Chromatogram of a 300 pesticides mix spiked by API 3200 LC/MS/MS system (100 ng/ml) XIC of +MRM (34 pairs): 253.2/171.2 Da from Sample 1 (5 ng/ml) of Triazines.wiff (Turbo Spray) Max. 7.5e4 cps. 1.3e5 1.3e5 1.3e5 1.2e5 1.2e5 1.1e5 1.1e5 1.0e5 9.5e4 9.0e4 8.5e4 8.0e4 Intensity, cps 7.5e4 7.0e4 6.5e4 6.0e4 5.5e4 5.0e4 4.5e4 4.0e4 3.5e4 3.0e4 2.5e4 2.0e4 1.5e4 1.0e4 5000.0 0.0 Triazines 6.9 3.5 4.0 4.5 5.0 5.5 6.0 6.5 7.0 7.5 8.0 8.5 9.0 9.5 10.0 10.5 11.0 Time, min Figure 3: Chromatogram of triazine pesticides at 5 ng / ml p 5

Table 2: List of triazine pesticides with retention times for each Triazines RT ( Min) Atrazine 8.5 Ametryn 7.8 Cyanazine 6.7 Desisopropyl-atrazine 5.4 Desethyl-atrazine 4.0 Hexazinon 6.9 Metazoachlor 7.8 Metolachlor 9.2 Metribuzin 7.4 Prometon 8.3 Prometryn 9.0 Propazine 8.6 Sebutylazine 8.4 Simazine 6.9 Terbuthylazine 8.6 Terbutryn 9.1 D5-atrazine (internal std) 7.7 XIC of +MRM (32 pairs): 229.2/172.4 Da from Sample 1 (20 ng/ml) of Phenyl ureas.wiff (Turbo Spray) Max. 3.0e5 cps. 9.5e5 9.0e5 Phenylurea Pesticides 8.5e5 8.0e5 7.5e5 7.0e5 6.5e5 6.0e5 Intensity, cps 5.5e5 5.0e5 4.5e5 4.0e5 3.5e5 3.0e5 7.0 2.5e5 2.0e5 1.5e5 1.0e5 5.0e4 0.0 2.5 3.0 3.5 4.0 4.5 5.0 5.5 6.0 6.5 7.0 7.5 8.0 8.5 9.0 9.5 10.0 10.5 11.0 11.5 12.0 Time, min Figure 4: Chromatogram of phenyl urea pesticides at 20 ng/ml p 6

Table 3: List of phenyl urea pesticides with retention times for each Phenyl Urea RT ( Min) Chlortoluron 7.6 Diflubenzuron 9.3 Diuron 8.0 Fenuron 4.6 Fluomethuron 7.6 Isoproturon 7.9 Linuron 8.5 Metabenzthiazuron 7.6 Metobromuron 7.7 Metoxuron 6.2 Monolinuron 7.4 Propanil 8.5 Siduron 8.6 Tebuthiuron 7.1 Thidiazuron 7.0 D6-Isoproturon (internal std) 7.6 XIC of +MRM (94 pairs): 239.2/72.1 Da from Sample 1 (10ng/mL) of Carbamates.wiff (Turbo Spray) 3.4e5 3.2e5 Max. 2.2e5 cps. Carbamates 3.0e5 2.8e5 2.6e5 2.4e5 2.2e5 7.4 Intensity, cps 2.0e5 1.8e5 1.6e5 1.4e5 1.2e5 1.0e5 8.0e4 6.0e4 4.0e4 2.0e4 0.0 1.0 2.0 3.0 4.0 5.0 6.0 7.0 8.0 9.0 10.0 11.0 12.0 13.0 Time, min Figure 5: Chromatogram of carbamate pesticides at 10 ng/ml p 7

Table 4: List of carbamate pesticides with retention times for each Carbamates RT ( Min) 3-Hydroxycarbofuran 5.0 Alanycarb 9.4 Aldicarb 6.0 Aldicarb-sulfone 2.2 Aldicarb-sulfoxide 1.6 Aminocarb 6.7 Bendiocarb 6.9 Benfuracarb 10.1 Benomyl 9.6 Butocarboxim 5.9 Butocarboxim-sulfoxide 1.5 Butoxycarboxim 2.1 Carbaryl 7.2 Carbofuran 6.9 Carbosulfan 11.5 Chloropropham 8.8 Dimepiperate 9.8 Dioxacarb 4.8 EPTC (S-Ethyl N,Ndipropylthiocarbamate) 9.2 Esprocarb 10.1 Ethiofencarb 7.4 Ethiofencarb-sulfone 4.2 Ethiofencarb-sulfoxide 4.2 Fenobucarb 8.3 Fenothiocarb 9.2 Fenoxycarb 9.2 Furathiocarb 10.1 Iprovalicarb 9.0 Isoprocarb 7.6 Methiocarb 8.4 Methocarb-sulfone 5.5 Methomyl 2.9 Oxamyl 2.3 Phenmedipham 8.2 Primicarb 7.5 Promecarb 8.5 Propamocarb 3.2 Propoxur 6.8 Pyributicarb 10.3 Terbucarb 9.8 Thiobencarb 9.6 Thiodicarb 7.5 Thiofanox 7.5 Thiofanox-sulfone 4.7 Thiram 6.7 Triallate 10.4 XMC 7.3 p 8

XIC of +MRM (68 pairs): 305.0/169.0 Da from Sample 1 (10ppb) of Organophosphorus.wiff (Turbo Spray) Max. 9.1e5 cps. 9.0e5 8.5e5 8.0e5 7.5e5 7.0e5 6.5e5 6.0e5 5.5e5 Intensity, cps 5.0e5 4.5e5 4.0e5 3.5e5 3.0e5 2.5e5 2.0e5 1.5e5 1.0e5 5.0e4 Organophosphorus Pesticides 13.2 0.0 2 4 6 8 10 12 14 16 Time, min Figure 6: Chromatogram of organophosphorus pesticides at 10 ng/ml Table 5: List of organophosphorus pesticide with retention times for each Organophosphorus RT ( Min) Acephate 3.1 Azinphos ethyl 12.6 Azinphos methyl 11.6 Chlorfenvinphos 13.1 Chlorpyrifos 14.6 Coumaphos 13.3 Demeton-s-methyl 8.5 Demeton-S-methyl-sulfone 7.3 Diazinon 13.2 Dichlorvos 9.9 Dicrotophos 7.8 Dimethoate 8.5 Famphur 11.1 Fenthion 13.2 Malathion 12.3 Mevinphos 9.1 Naled (Dibrom) 11.3 Parathion-ethyl (Parathion) 13.1 Parathion-methyl 7.3 Phorate 13.4 Phorate sulfoxide 10.8 Pirimiphos-ethyl 14.2 Pirimiphos-methyl 13.5 Sulfotep 13.1 Sulprofos 14.4 p 9

Organophosphorus RT ( Min) Tetrachlorvinphos 12.8 Triazophos 12.4 Tokuthion (Prothiophos) 15.1 EPTC (Internal std) 12.9 XIC of -MRM (38 pairs): 239.0/193.0 Da from Sample 1 (10ppb) of Acidic pesticides.wiff (Turbo Spray) Max. 2.0e5 cps. 2.6e5 2.5e5 2.4e5 2.3e5 2.2e5 2.1e5 2.0e5 1.9e5 1.8e5 1.7e5 1.6e5 Intensity, cps 1.5e5 1.4e5 1.3e5 1.2e5 Acidic Pesticides 1.1e5 1.0e5 9.0e4 8.0e4 7.0e4 6.0e4 5.0e4 4.0e4 3.0e4 2.0e4 1.0e4 0.0 3.0 4.0 5.0 6.0 7.0 8.0 9.0 10.0 11.0 12.0 13.0 14.0 Time, min Figure 7: Chromatogram of acidic pesticides at 10 ng/ml Table 6: List of acidic pesticides with MRM transitions and retention times for each Acidic Pesticides RT ( Min) 2,4,5-T 10.5 2,4,5-TP 11.5 2,4-D 8.6 2,4-DB 11.8 2,4-DP (Dicloprop) 10.2 Bentazon 6.5 Bromoxynil 8.8 Clopyralid 3.4 Dicamba 5.6 Dinoterb 12.1 Dinoseb 12.1 Fluoroxypyr 6.6 Imazapyr 4.7 Ioxynil 10.2 MCPA 9.0 MCPB 11.9 MCPP 10.6 PCP 12.8 Triclopyr 9.6 12.1 p 10

Please note that the results presented above were obtained using a single instrument and single set of standards and samples. Prior to production use, the method should be fully validated with real samples, and the results here may not be typical for all instruments. Variations in LC column properties, chemicals, environment, instrument performance and sample preparation procedures will impact performance, thus these results should be considered as informative rather than representative. System Requirements In order to run this method as outlined above, the following equipment and reagents are required: An AB SCIEX 3200 Series (3200 QTRAP or API 3200 ), 4000 Series (4000QTRAP or API 4000 ), AB SCIEX QTRAP 5500 or AB SCIEX Triple Quad 5500 LC/MS/MS system A Shimadzu Prominence 20A LC System with reservoir tray and bottles, system controller CBM-20A, 100 µl mixer, 2 isocratic pumps LC-20AD, 3 channel degasser autosampler SIL-20AC, column oven CTO-20AC or Agilent 1100/1200 LC system with binary pump G1312A (without static mixer), well plate autosampler, and thermostated column oven. Pesticide Standards (www.sigmaaldrich.com) Pesticide Internal Standards (www.sigmaaldrich.com) LC/MS-grade water, methanol, acetonitrile, ammonium acetate, ammonium formate Phenomenex Synergi 4µ Fusion-RP 80A 50 x 2 mm HPLC column for carbamates and triazines Phenomenex Synergi 2.5 µm Fusion 100 Å, 50 x 2 mm HPLC column for the pesticide screening method 1.5 ml Eppendorf tubes A Centrifuge, able to accommodate Eppendorf tubes and run at 14000 rpm Pipettes and standard laboratory glassware Both Phenomenex Fusion HPLC columns come standard with this imethod test kit. This method can also be run on other HPLC systems, given that they are supported for use by the Cliquid Software and the retention times are updated to reflect the configuration used. Ordering Information Product Name imethods Test for Pesticide Screening V.2.0 for Cliquid Software Part Number 1037144 While the information provided above outlines the instrument requirements and expected results obtainable from the AB SCIEX imethod Test for Pesticide Screening, the results obtained do require some experience with LC/MS/MS and sample preparation procedures. As such, web-based and on-site training are available to assist in the deployment of the imethod test and are recommended for inexperienced users. Please consult your local sales representative for more details. Important Note The purchase and use of certain chemicals listed above may require the end user to possess any necessary licenses, permits or approvals, if such are required in accordance with local laws and regulations. It is the responsibility of the end user to purchase these chemicals from a licensed supplier, if required in accordance with local laws and regulations. The suppliers and part numbers listed below are for illustrative purposes only and may or may not meet the aforementioned local requirements. Legal Acknowledgements/Disclaimers The imethod Test described above has been developed by AB SCIEX to provide all the sample prep and instrument parameters required to accelerate the adoption of this method for routine testing. The performance of this method will need to be verified in a given lab due to potential variations in instrument performance, maintenance, chemicals and procedures used, technical experience, sample matrices and environmental conditions It is the responsibility of the end user to make adjustments to this method to account for slight differences in equipment and/or materials from lab to lab as well as to determine and validate the performance of this method for a given instrument and sample type. Aworking knowledge of Analyst Software may be required to do so. p 11

The suppliers identified in this document are provided for information purposes only and is not intended to be an exhaustive representation of all manufacturers or suppliers of the referenced product. AB SCIEX makes no warranties or representations as to the fitness or the continued fitness of a specific product by any of the manufacturers/suppliers referenced herein or the supplier. AB SCIEX assumes no responsibility or contingent liability, including indirect or consequential damages, for any use to which the purchaser may put the referenced suppliers products, or for any adverse circumstances arising therefrom. For Research Use Only. Not for use in diagnostic procedures. 2010 AB SCIEX. The trademarks mentioned herein are the property of AB Sciex Pte. Ltd. or their respective owners. AB SCIEX is being used under license. Publication number: 1160210-02 p 12